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| WTO Dispute
Biotechnology: Addressing Key Trade and Sustainability Issues
B.1 Environmental, health-related and socio-economic
considerations
Q2 Are GMOs harmful to the environment?
Existing evidence on the environmental impacts of GMO
production does not yield proof of systemic adverse effects of the
technology; however, similarly to the above-mentioned health concerns,
some argue that not enough long-term studies have been carried out
to lay to rest the various concerns that have been highlighted. In
particular, many suggest that there is a need for an appreciation
and study of the distinct environmental conditions that prevail in
different parts of the world, including the ecosystems and soils in
tropical, biodiversity-rich developing countries. It has also been
stressed that efforts to assess the adverse impacts of GM crops must
use conventional agricultural crops as the frame of reference or counterfactual.
GM crops can have two types of environmental impacts,
namely a direct impact that derives from the GMO itself and indirect
impacts that stem from the different management choices that the new
crop offers to the farmer.
Transfer of genes within species occurs naturally in
the wild and in agricultural fields. In the context of GM crops, however,
such gene transfer poses unique challenges because of the possible
transfer
of transgenic DNA to non-modified plants. Such transfer would decrease
the ability to control or regulate the spread of modified crops, and
could affect biodiversity or cultural and social values (see Biotech
Headline 2). Environmental advocates have cautioned that the transfer
of genes from GM plants which have been genetically engineered to
withstand herbicide applications could lead to the creation of superweeds
if the genes were taken up by related wild varieties of the same species.
They warn that these superweeds could be more difficult
to kill, require more or stronger herbicides and could become invasive
with adverse effects on agricultural biodiversity. A related concern
is that GM plants themselves will become weeds, or could become invasive
(Conner et al., 2003) (see also Q3).
| BIOTECH
HEADLINE 2: Mexican Maize
In October 2000, Ignacio Chapela and David Quist, researchers
from the University of California at Berkeleys College
of Natural Resources, found transgenic DNA in maize grown in
a remote area in the state of Oaxaca, Mexico. The Mexican government
subsequently performed and in September 2001 released its own
research confirming that, despite a moratorium on environmental
release of GM maize in Mexicosince 1998, transgenic DNA had
in fact made its way into Mexican maize landraces. In November
2001, Chapela and Quist published their research findings in
the scientific journal Nature. The discovery ignited a controversy
fuelled by the fact that Oaxaca is the so-called centre
of origin and diversity of maize, where it was domesticated
from a weed named teosinte hundreds of years ago.
Environmentalists, farmers and local communities from Mexico
and around the world asked how the local races became contaminated
and questioned what the potential implications could be for
the local communities and genetic diversity. Greenpeace, the
ETC Group and other international civil society groups suggested
that permanent loss of biodiversity may result, and local communities
made links between the contamination and systemic political
problems in rural areas. As a result, in April 2002, twenty-one
indigenous communities from Oaxaca and three Mexican environmental
groups petitioned the North American Commission for Environmental
Cooperation (CEC) to assess the impacts of transgenic contamination
of Mexican maize races. The CEC was created under the North
American Agreement on Environmental Cooperation (NAAEC), an
environmental side agreement to the North American Free Trade
Agreement (NAFTA) between Mexico, Canada and the US.
The final CEC report, which was released in November 2004,
traced the arrival of the GMOs in Oaxaca back to imports of
maize from the US, where GM maize makes up approximately one-third
of the maize crop and is not segregated from non-modified maize.
Although the maize was only intended for consumption,
small-scale farmers planted the seeds. The report concludes
that there is no reason to expect that a transgene would
have any greater or lesser effect on the genetic diversity of
landraces or teosinte than other genes from similarly used modern
cultivars, suggesting that, from a scientific point of
view,
transgenic maize does not threaten genetic diversity more than
other methods of modern agriculture such as hybridisation. At
the same time, the report stresses the cultural, symbolic and
spiritual values of maize for many Mexicans, in particular the
campesinos (or small-holder farmers) who perceive GM maize
as a
direct threat to political autonomy, cultural identity, personal
safety and biodiversity. The report adds That sense
of harm is independent of its scientifically studied potential
or actual impact upon human health, genetic diversity, and the
environment.
Based on these concerns, and using a precautionary approach,
the CEC report recommends that the GM maize planting moratorium
should be continued and strengthened by minimising the
import of living transgenic maize grain from countries that
grow transgenic maize commercially. The US and Canada
issued strong public statements criticising the report and,
in particular, what they regard as a contradiction between the
scientific key findings and the recommendations. The publication
of a new study in the Proceedings of the National Academy of
Sciences in August 2005, showing no evidence of GMOs in more
than 150,000 seeds taken from 870 plants in Oaxaca in 2003 and
2004 has, for now, calmed demands for measures to be taken.
Sources: CEC (2004); Ortiz-Garcia et al. (2005); Quist and
Chapela (2001).
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Gene flow from plants which have been genetically modified
to produce pharmaceutical, chemical or industrial compounds could
lead to the inadvertent spread of chemical compounds or medicines
to soils, ecosystems and other plants. For example, in 2002, seeds
from plants genetically modified to generate an animal vaccine germinated
in the field from which they had earlier been harvested in the US,
and mixed with soybeans that were subsequently grown on the land (Cohen,
2002). The soy was destroyed as the impacts of the vaccine on human
health and the environment were unknown, and because ProdiGene
the Texas-based biotech company that had developed the GM maize
had not taken human consumption or environmental release into account
in its risk assessment. However, given the unique nature of these
plants, most regulators and actors in these industries agree that
they need to be carefully segregated to prevent gene transfer to other
crops and to the environment (Nuffield Council, 2004). Research on
the environmental effects of these crops is in its infancy.
Genetic Use Restriction Technologies (GURTS) have been
proposed by the biotech industry as a possible means to prevent unintended
gene flow. GURTS can be used to genetically alter seeds to be sterile
and thus prevent cross-fertilisation. The technology dubbed
terminator technology by its critics has attracted
fierce criticism from environment, farmer and indigenous groups who
warn that inhibiting a plants ability to reproduce could have
adverse effects on rural livelihoods by preventing reuse of the seeds
by farmers and on biodiversity by risking to transfer the trait to
wild varieties. As a result, a de facto moratorium on field trials
of GURTS was instituted by the Parties to the CBD in 2000 when countries
recommended that products incorporating such technologies should
not be approved by Parties for field testing [
] and for commercial
use until potential environmental and socio-econoimc impacts
have been assessed (CBD, 2000).
GM crops can also have direct impacts on non-target
species that consume them or their pollen. Crops which use Bacillus
thuringiensis, a soil bacterium that kills many of the worm-like insects
that destroy crops, is a case in point. While Bt saves the crop from
pests that destroy the crop, it could also hurt other harmless worm-like
insects that are found in the fields (see Biotech Headline 3). There
is also the possibility that insects will become immune to the Bt
toxin since such resistance would provide them with an evolutionary
advantage in the presence of widespread Bt use. This could have adverse
longterm effects on the invasiveness of these insects in the environment
and on farms, because use of Bt including through sprays and
non-GM methods is one of the most effective, cheapest and least
environmentally harmful ways to tackle the spread of pests. This problem
has not emerged thus far possibly owing to the requirement
in many countries to have small areas of non-Bt plants (refuges)
near any Bt fields to minimise evolutionary advantages any Bt-resistant
insects would have (IFATPC, 2004).
BIOTECH
HEADLINE 3: Monarch Butterflies
On 20 May 1999, the journal Nature published research by leading
scientists at Cornell University showing that monarch butterfly
larvae that ate milkweed leaves coated with pollen from GM maize
ate less, grew more slowly and suffered a higher mortality rate
than those that ate non-coated leaves. The larvae in
question are small caterpillars that grow into the endangered
and popular monarch butterflies, and the suggestion that they
could be jeopardised by genetically modified Bt maize raised
widespread concern.
Several studies released after the initial report have shown,
however, that the actual risk posed to monarch butterflies by
Bt maize was minimal. Bt is inserted into maize through genetic
modification because it is selectively toxic to lepidopteran
(larval or wormlike) insects. While the monarch butterfly larvae
is such an
insect, and was thus affected by consuming pollen from Bt maize
in the lab, scientists concluded that under real world
conditions butterfly larvae are unlikely to encounter Bt maize
pollen in nature. Butterfly larvae feed on milkweed, a weed
which farmers keep out from the fields of agricultural crops
such as maize. Monarch butterflies in particular prefer to eat
milkweed near open meadows, ditches and pastures where they
fly and deposit their larvae at a distance from the fields.
Maize pollen cannot reach the milkweed plants in the ditches
on which the larvae like to feed because it is too heavy. Field
studies in Iowa and in agriculture departments of a number of
US universities, along with a 2001 report from the US Environmental
Protection Agency (USEPA), confirmed that the lack of milkweed
in maize fields and the preference of butterflies for milkweed
far from maize fields decrease the presence of Bt pollen in
butterfly diets. They also pointed out that maize pollen is
released in five to ten-day intervals when most butterfly larvae
are not present because of migratory patterns, and that monarch
butterflies do not like to eat pollen and tend to avoid pollen-tainted
milkweed leaves, Bt or not. For all these reasons, during field
trials scientists found that it was rare to have a combination
of maize, pollen, milkweed and monarch butterfly larvae. Biotech
supporters also stress that even if this combination were to
occur, factors such as habitat destruction and the use of broad
spectrum herbicides pose far greater threats to the Monarchs.
Sources: Losey et al. (1999); USDA (2004).
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In addition, GM crops change the options that are available
to farmers for pest and weed management. The use of the new crops
can lead to farming practices that affect the agricultural environment,
including different kinds and quantities of pesticides and herbicides,
resulting in indirect effects of the new crops characteristics
on the surrounding environment.
GM crops can change the way herbicides are applied to
the crop (FAO, 2004). A single, broad-spectrum herbicide, such as
glyphosate, is often sprayed on plants that have been genetically
modified to be tolerant to herbicides in order to kill the weeds that
surround the plants. Glyphosate has been advocated as a relatively
benign herbicide since it rapidly degrades in the soil and has a low
level of toxicity. Herbicide-tolerant crops are also claimed to require
fewer applications of herbicides than conventional crops. However,
whether the GM plants reduce overall herbicide use and persistence
in the soil depends on a variety of factors, such as the suitability
of the plant variety to the region, the extent of pre-GM investment
in chemical herbicides and fertilizers, and the adaptation of pests
and weeds to the treatment. Changes in herbicide application can also
have impacts on non-target weed and plant life and the insects and
animals that eat them. The effectiveness of the new herbicide in killing
weeds (while allowing the crop itself to survive) can eliminate most
weed cover and thereby reduce soil and agricultural biodiversity and
harm non-target species that feed on these weeds. The
largest agricultural biodiversity study to date, known as the UK Farm
Scale Evaluations, concluded that while the use of GM crops does change
the mix of weeds that survive herbicides, the impacts
on agricultural biodiversity vary between crops and the particular
herbicides used, and are within the normal scope of biodiversity impact
variation within crops (see Biotech Headline 4).
More broadly, there are fears that adoption of GM plant
varieties could encourage a tendency towards monocropping, intensive
farming and mechanisation of agriculture with adverse impacts on biodiversity.
Supporters of GM crops argue that in fact it could do the opposite
by reducing the need for chemical inputs and mechanised operations,
with positive impacts on water supplies, pesticide use, pesticide
residues, farmer health and food safety. For example, the fact that
herbicide-tolerant plants need not be ploughed around for removal
of weeds means that no-till practices can be adopted,
which in turn can preserve soil, prevent desertification and stripping
of soil nutrients and reduce greenhouse gas emissions. However, it
also needs to be borne in mind that, particularly in developing countries,
GM crops and their accompanying herbicide or pesticide treatments
might become a substitute for what has so far been herbicide and pesticide-free
production, rather than an alternative to herbicide and pesticideintensive
production as it is in developed countries.
The environmental implications of GM animals have also
been raised. It is feared that the increased use of a few uniform
GM animals could reduce animal biodiversity, and that the spread of
genes from
GM animals would be difficult to control, owing to the animals
mobility and reproductive patterns. Furthermore, there are concerns
that unintended effects of genetic modification, similar to those
described above for plants, could lead to novel changes to the animal
physiology that could be difficult to predict, anticipate or address.
In this context, transgenic fish have raised particular
concerns (Pew Initiative, 2003). It is feared that GM fish might escape
from fish farms and spread novel traits into the ecosystem by breeding
with wild
relatives, thereby impacting on marine biodiversity. Transgenic fish
that escape into natural ecosystems could also be an environmental
nuisance by becoming an invasive species. Scientists are attempting
to reduce these risks by sterilising transgenic fish (Pew Initiative,
2003).
Research is also under way to genetically modify insects
in order to reduce invasive populations, such as fruit flies, through
selective sterilisation. There are also more ambitious projects to
change other
characteristics of insects to make them less problematic for
example, to decrease their tendency to spread viruses. While such
changes have been advocated by some as a means of ensuring human and
in some cases animal health, the complicated relationship between
insects, bacteria, animals and ecosystems, along with the difficulty
in controlling the spread of insects, has raised concerns about the
unintended spread of GM insects and the potential implications on
their invasiveness and impacts. As such, no GM insects have been released
to date (Pew Initiative, 2004).
At the same time, the most promising field of animal
biotechnology the use of biotechnology to develop vaccines
and reproductive techniques could in fact improve animal health
and diversity (MacKenzie, 2005).
| BIOTECH
HEADLINE 4: UK Farm Scale Evaluations
In 1999, the UK government asked an independent consortium
of researchers to investigate how growing four types of herbicide-tolerant
GM crops might affect the abundance and diversity of farmland
wildlife compared with growing conventional varieties of the
same crops. The resulting study, called the Farm Scale Evaluations
(FSE), lasted five years, cost around GBP6 million and was the
largest field experiment ever conducted on farmland ecology.
The research pointed to differences in impacts on weed, insect
and other farm wildlife populations between GM and non-GM crops.
The report found that these differences could be attributed
to the type and way herbicides were applied to the GM and non-modified
crops rather than the genetic modification itself.
More specifically, it was found that GM beet and spring rape
(canola) crops had fewer weeds, weed seeds, bees and butterflies,
but more springtails (an insect that feeds on decaying plants).
On the other hand, growing GM maize was better for many groups
of wildlife than conventional maize because the GM crops had
more weeds, seeds, bees and butterflies and springtails. Regarding
winter rape, the GM and conventional crops had the same number
of weeds overall. The GM crop was found to have more grass weeds
and seeds but fewer broad-leaved weeds and seeds, resulting
in fewer butterflies and bees, who feed predominantly on broad-leaved
weed seeds, but more springtails.
Anti-GM campaigners, along with the UK and European media,
hailed the study as proof that GM crops should be abandoned.
These results are another good reason to abandon all plans
for growing GM oilseed rape in the UK, GeneWatch Director
Sue Mayer said. Others suggested that the results showed that
GM crops do not pose a threat in themselves to farm biodiversity;
rather, GM-conventional comparisons test the relative impact
of different herbicide uses given that GM crops offer new herbicide
choices. They also pointed out that in all four cases there
was only one herbicide spray for the GM crops, compared to multiple
sprayings for conventional crops, delivering positive environmental
impacts given that herbicides can also damage the environment
in the long term. Also, they noted that differences in impacts
on biodiversity were greater among the four types of crops than
between GM and conventional varieties of one crop, implying
that the choice of crop along with the type of crop rotation,
pesticide use and agricultural intensity may have more
significant impacts on farmland wildlife than the different
herbicide uses resulting from GM crops.
Sources: AgBioWorld (2003); GeneWatch (2005); www.defra.gov.uk/environment/gm/fse/.
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